{a novel carbon paste electrode based on nitrogen-doped … · 2017-12-04 · new material for...

J. Serb. Chem. Soc. 82 (11) 1259–1272 (2017) UDC 544.6.076.32–039.26:547.563’448: JSCS–5038 547.497.1+543.552+544.6 Original scientific paper

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A novel carbon paste electrode based on nitrogen-doped hydrothermal carbon for electrochemical determination of

carbendazim ANA KALIJADIS1*, JELENA ĐORĐEVIĆ1#, ZSIGMOND PAPP2#, BOJAN JOKIĆ3,

VUK SPASOJEVIĆ1, BILJANA BABIĆ1 and TATJANA TRTIĆ-PETROVIĆ1# 1Vinča Institute of Nuclear Sciences, University of Belgrade, P.O. Box 522, 11001 Belgrade,

Serbia, 2Faculty of Biofarming, John Naisbitt University, Maršala Tita 39, 24300 Bačka Topola, Serbia and 3Faculty of Technology and Metallurgy, University of Belgrade,

Karnegijeva 4, 11000 Belgrade, Serbia

(Received 28 December 2016, revised 28 April, accepted 15 Мay 2017)

Abstract: In this work, a new carbon paste electrode, prepared from nitrogen- -doped hydrothermal carbon (CHTCN) was applied for the electrochemical detection and determination of carbendazim fungicide. CHTCN samples with the nominal nitrogen content 0.05–0.5 wt. % in glucose precursor were pre-pared by simple, low-cost synthesis with the accompanying carbonization to 1273 K. The presence of nitrogen in CHTCN samples was confirmed by ele-mental analysis. Characterization of CHTCN as material for carbon paste elec-trode was achieved by cyclic voltammetry measurement of the Fe(CN)6

3-/4- redox couple. The results showed that best electrochemical response was obtained from the sample with a nominal nitrogen concentration of 0.1 wt. % and with tricresyl phosphate as a binder. During the development of a differ-ential pulse stripping voltammetric method for carbendazim determination applying new electrode, the following experimental parameters were studied: the sort and amount of binding liquid, the effect of pH, accumulation potential and accumulation time. Under optimal conditions, the electrode offered linear-ity in the wide concentration range from 25 to 490 ng cm-3 and an estimated detection limit of 1.21 ng cm-3. Moreover, the electrode showed good stability, high selectivity and satisfactory anti-interference ability. Finally, the developed method was successfully applied for the determination of carbendazim traces in spiked tap and river water samples.

Keywords: method development; fungicide; electrochemical determination; stripping voltammetry; tricresyl phosphate.

* Corresponding author. E-mail: [email protected] # Serbian Chemical Society member. https://doi.org/10.2298/JSC161228053K

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Available on line at www.shd.org.rs/JSCS/

1260 KALIJADIS et al.

INTRODUCTION Pesticides represent a significant part of the protection of agricultural pro-

duction. Their application manages the problems with unwanted pests or weeds, but it, unfortunately, constitutes a risk of the environment pollution. Pesticides are generally toxic for living organisms even at low concentrations. Although many pesticides have been forbidden or restricted to use in different regions, many of them are still frequently used for pest or weed control.1

Carbendazim is a systemic benzimidazole fungicide (IUPAC name methyl- -1H-benzimidazol-2yl-carbamate) which was regularly used to prevent and cure different diseases of the crop. It was applied to prevent some illnesses on bananas, apples, tomatoes, cereals, etc. It could persist for a long time when applied in the environment and its degradation is rather slow.2–4 The toxicity of carbendazim is well documented.5 It shows harmful effects on human health and environment, therefore, its determination is really important.

Several techniques have been used for quantitative determination of carben-dazim, first of all, chromatography,6–12 spectrophotometry,13,14 spectrofluorim-etry,15,16 Raman spectroscopy,17 flow-injection chemiluminescence18 and enz-yme-linked immunosorbent assay (ELISA).19 On the other hand, the electro-chemical methods represent an alternative to these techniques and offer advent-ages, such as good selectivity, easier sample preparation, faster analysis and sensitivity which could be comparable to chromatography.20 Several papers were published about voltammetric determination of carbendazim using different unmodified21,22 and modified23–28 carbon-based electrodes, including also carbon paste-based electrodes.22,23,26

Carbon paste electrode (CPE) is generally a mixture of graphite (carbon) powder and liquid binder (e.g., silicone oil (SO), paraffin oil (PO), tricresyl phos-phate (TCP)) packed into adequate electrode body. CPEs represent a very pop-ular type of sensors which offers simple laboratory preparation, low price, broad potential window, low background current, unique surface characteristics, usually low toxicity, high sensitivity, and applicability for the monitoring of elec-trochemically active inorganic and organic environmental pollutants.29–32

Hydrothermal carbonization (HTC) has been developed recently as a mild and promising strategy to obtain the functional carbonaceous nanostructures from cheap biomass. To convert biomass to carbon, HTC has been considered as an efficient method operated in an environmentally friendly process. The typical HTC carbons are micrometer-sized, spherically shaped particles, which are pro-duced by HTC of soluble, non-structural carbohydrates.33 Importantly, the vers-atility of HTC makes it quite easy to achieve heteroatom doping carbon mat-erials. Nitrogen-doped carbon materials have gained an increasing interest in the last decade, mainly because doping carbonaceous materials with nitrogen is an effective way of modifying the surface chemistry of materials and improving

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NEW MATERIAL FOR CARBON PASTE ELECTRODE 1261

their electrochemical properties.34,35 Nitrogen-containing hydrothermal carbons have been prepared from different types of biomasses or derivatives such as chitin, chitosan, glucosamine, microalgae and so on.36–38 The nitrogen-free pre-cursors and nitrogen containing molecules such as ovalbumin, glycine, and ethyl-enediamine have also been employed in the preparation of nitrogen-containing HTC derived carbons.39–41 Nitrogen incorporated into carbon materials can not only act as an electron donor due to its five valence electrons which result in a shift of the Fermi level to the valence band but also introduce functional groups containing nitrogen and oxygen atoms.42 Hydrothermal carbons doped with nit-rogen have been already tested as electrode capacitors and electrocatalyst for oxygen reduction reaction.43–45 Strelko et. al46 suggested that the influence of nitrogen heteroatoms on the catalytic activity of carbons in electron transfer reactions may be explained on the basis of the suggestion that the insertion of nitrogen atoms into the graphite lattice lowers the band gap, thus producing higher electron (charge) mobility and a lowering of the electron work function at the carbon/ liquid (gas) interface, compared with pure carbons.

In our previous work, we have successfully synthesized boron doped carbon-ized hydrothermal carbon based on glucose as a precursor and applied as a mat-erial for carbon paste electrode.47 We found that the modified structural and surface characteristics are responsible for good electron transfer property of a carbon paste electrode based on boron-doped samples with a nominal boron concentration range from 0.2 to 0.6 wt. %. Based on these results and literature review we decided to continue to examine the influence of other dopants, espe-cially nitrogen, on properties of hydrothermal carbon and its further application in the field of electrochemistry, especially electroanalysis.

In this work a differential pulse stripping voltammetric (DPSV) method was developed for the determination of carbendazim using a CPE based on newly synthesized carbonized nitrogen-doped hydrothermal carbon (CHTCN) and TCP as a binding liquid. CHTCN samples were synthesized by introducing melamine into glucose precursor solution, to obtain a nominal concentration of nitrogen from 0.05 to 0.5 wt. %. The basic characterization of the new electrodes was done using the cyclic voltammetry of the Fe(CN)6

3–⁄4– redox couple. After the DPSV method optimization, the target compound was successfully determined in model solutions, tap- and river water samples.

EXPERIMENTAL Chemicals

Methanol, melamine, K3[Fe(CN)6], D(+)-glucose, silicone oil, paraffin oil, tricresyl phos-phate, phosphoric, boric and acetic acids, potassium chloride, potassium sulfate, and sodium hydroxide were purchased from Sigma-Aldrich (St. Louise, MO, USA). Deionized water was prepared using a Millipore purification system (Bedford, MA, USA).

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Carbendazim (99 % purity) was obtained from Fitofarmacija a.d. (Zemun, Serbia). The stock solution of 333 μg cm-3 concentration was made by dissolving the pesticide in methanol and was kept in dark at –18 °C before analysis. Britton-Robinson buffer solutions were pre-pared from a stock solution containing 0.04 M phosphoric, boric and acetic acids, respectively by adding 0.2 M sodium hydroxide to obtain the required pH value. Preparation of CHTCN samples

To produce hydrothermal carbons, a water solution of D(+)-glucose (2 M) was prepared and placed into 50 cm3 Teflon®-lined stainless steel autoclave. Melamine was used as a source of nitrogen and it was added to the precursor solution to obtain the nitrogen concentration of 0.05, 0.1 and 0.5 wt. %. After sealing, the autoclave was heated in a programmable oven for 24 h at 453 K. The obtained black solid powders were abundantly washed with deionized water and alcohol and then dried at 353 K for 24 h. Pyrolysis of CHTCN samples was per-formed in a flow of high-purity nitrogen up to 1273 K, at the heating rate of 5 K min-1. Obtained samples were marked as CHTCN0.05, CHTCN0.1 and CHTCN0.5, (subscripts denote nominal nitrogen concentration, i.e., concentration in glucose precursor solution). Instruments

The LECO elemental analyser, model CHNS-628, was used for the elemental analysis of CHTCN samples. The morphology of CHTCN was studied by field emission scanning elec-tron microscopy (FESEM) TESCAN Mira3 XMU at 20 kV.

A 797 VA Computrace analyzer (Metrohm) controlled by 797 VA Computrace software version 1.2 was applied for all voltammetric measurements. A three-electrode system included an Ag/AgCl electrode (in saturated KCl) as a reference, platinum wire as auxiliary and differ-ent types of CPEs based on CHTCN as working electrode. All electrochemical experiments were carried out in a conventional voltammetric cell (with an operating volume of 10 cm3) at room temperature (296±1 K). Before starting a new set of measurements the supporting elec-trolyte was deaerated by suprapure nitrogen for 5 min. Electrode preparation

CPEs were prepared by hand mixing of 0.25 g CHTCN samples with 0.11 g of binder (TCP, SO or PO) using pestle and mortar, and then packed into the Teflon® holder (2 mm diameter). Prepared CPEs were marked as CPE/CHTCN0.05, CPE/CHTCN0.1 and CPE/ /CHTCN0.5. Before starting a new set of experiments about 0.5 mm of carbon paste was mechanically squeezed out from the electrode holder and polished on a wet filter paper. During the optimization of the amount of TCP four electrodes were prepared with 0.25 g of CHTCN0.1 and 20, 25, 30 and 40 wt. % of the binder using identical preparation procedure. Cyclic voltammetry (CV), differential pulse voltammetry (DPV) and differential pulse stripping voltammetry (DPSV)

CV experiments were used for preliminary characterization of the working electrodes, including testing of the effect of type and amount of the binding liquids, and also for the investigation of electrode aging. Measurements were performed in 1.0 mM Fe(CN)6

3-/4-/0.1 M K2SO4 solution in the potential range from –0.5 to 1.0 V, using scan rate of 50 mV s-1. DPV was used to investigate the effect of pH on the carbendazim oxidation at the CPE/CHTCN0.1 electrode in model solutions containing Britton–Robinson buffer as supporting electrolyte in the pH range from 2.0 to 8.0. DPSV was used for quantitative determination of carbendazim. Its parameters were carefully optimized and were as follows: start potential –0.2 V; end potential 1.2 V; accumulation potential (Eacc) = –0.15 V; accumulation time (tacc) = 80 s and

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scan rate = 100 mV s-1. The river water sample was collected from river Danube in village Vinča (12 km far from Belgrade). The water samples were filtrated through 0.45 µm filter to remove the suspended particles and storied in a glass bottle at 277 K. Tap water was analyzed without any sample pretreatment. Before analysis, the water samples were spiked with carben-dazim (50 ng cm-3) and diluted with Britton–Robinson buffer pH 3.0 in the volume ratio 1:1.

RESULTS AND DISCUSSION

Electrode characterization and composition optimization Results obtained by elemental analysis confirmed the presence of nitrogen in

CHTCN samples (Table I). Using melamine as a nitrogen source allows the obtaining of the final nitrogen concentration of 2.8, 3.2 and 4.5 wt. % in carbon-ized hydrothermal carbons with the initial concentration of nitrogen in glucose precursor solution of 0.05, 0.1 and 0.5 wt. %, respectively.

TABLE I. Summary of the cyclic voltammetric data for Fe(CN)63-/4- redox system at

CPE/CHTCNs together with elemental analysis results Sample ΔEp / mV ipa / µA ipa / ipc cC / wt. % cN / wt. % cH / wt. % CPE/CHTCN0.05 384 47 0.866 93.3 2.8 1.9 CPE/CHTCN0.1 210 85 0.958 92.6 3.2 1.7 CPE/CHTCN0.5 301 33 0.768 90.8 4.5 1.6

The redox couple of Fe(CN)63–/4– was chosen to characterize the electron

transfer properties of CPEs based on different CHTCN samples. Fig. 1 presents cyclic voltammograms of Fe(CN)6

3–/4– redox couple for three obtained CPE/ /CHTCN electrodes with TCP as a binder. CPEs based on pure carbonized hyd-rothermal carbon were excluded from the examination because the previous results47 showed that poor electrochemical behaviour was obtained independently of the binder type. However, it can be noted that all three CPE/CHTCNs show very well defined the electrochemical response toward Fe(CN)6

3–/4–. In order to clarify the electrochemical response of CPE/CHTCNs better, some derived feat-ures are given in Table I. It is obvious that CPE/CHTCN0.1 exhibited the smallest

Fig. 1. Cyclic voltammograms of Fe(CN)6

3-/4- redox couple in 0.1 M K2SO4 obtained at three different car-bon paste electrodes: CPE/CHTCN0.05, CPE/CHTCN0.1 and CPE/CHTCN0.5 with TCP as a binder. Potential range from –0.5 to 1.0 V and scan rate of 50 mV s-1.

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potential differences between oxidation and reduction peaks (ΔEp), the highest peak current intensity (ipa) and the highest peak current ratio (ipa/ipc) of 0.958, suggesting a faster electron transfer kinetics in comparison with other two CPE/ /CHTCNs.

It can be noticed that there is no linear relationship between the nitrogen content and electrochemical response of examined CPEs. CPE /CHTCNs with lowest and highest nitrogen content have much poorer electrochemical para-meters compare to the electrode with the middle value of nitrogen content. Com-parison of results for CPE/CHTCN0.1 with the results obtained for CPE based on boron-doped47 carbonized hydrothermal carbon shows that the nominal nitrogen content of 0.1 wt. % provides a CPE with much-improved electrochemical char-acteristics. Also, these results confirmed suggestion of nitrogen catalytic activity on electron transfer reactions, which originates from higher electron mobility.46

Additionally, the examinations of the binder type influence toward Fe(CN)63–/4–

showed that both other binders SO and PO induced the worsening of CPE/ /CHTCNs electrochemical behaviour, especially PO comparing to TCP. As an example of that cyclic voltammograms of Fe(CN)6

3–/4– redox couple for CPE/ /CHTCN0.1 are presented in Fig. 2. The examination relating to the binder type influence were also performed with CPE/CHTCN0.05 and CPE/CHTCN0.5. Unfor-tunately, any improvement of the electron transfer properties of the examined CPEs was not noticed. All cyclic voltammograms are with well-defined anodic and cathodic peak for the above redox system. The position and intensity of the signals were clearly dependent on the binder type. The advantage of the TCP was evident because it offered the most reversible behaviour, most intense peak current together with the low residual current. Furthermore, ΔEp, ipa/ipc values for an electrode with SO and PO as binders are 517 mV, 0.912 and 889 mV, 0.746, respectively. Therefore, the TCP was chosen as a binder for the following expe-riments. For the optimization of TCP content in CPE/CHTCN0.1, paste mixtures with 20, 25, and 40 wt. % of TCP were prepared and CV curves of Fe(CN)6

3–/4–,

Fig. 2. Cyclic voltammograms of 1 mM Fe(CN)6

3-/4- redox couple in 0.1 M K2SO4 at CPE/CHTCN0.1 prepared with the different type of binder: PO, SO or TCP. Potential range from –0.5 to 1.0 V, using scan rate of 50 mV s-1.

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the redox couple, were recorded and compared with the previously obtained CV curve with carbon-to-binder ratio: 0.25 g to 0.11 g, which represents approx-imately 30 wt. % of TCP. The electrochemical process was most reversible at the CPE/CHTCN0.1 with 30 wt. % of TCP, with the acceptable background current. The obtained results showed (Fig. S-1 of the Supplementary material to this paper) that in comparison to CPE/CHTCN0.1 with 30 wt. % of TCP, the electrode with 20 wt. % of TCP gave more intense signals, but with very intense back-ground current. On the other hand, an electrode with 25 wt. % of TCP gave sig-nificantly lower signal intensity, together with the very favourable background. 40 wt. % of TCP had practically a liquid consistency and it was not possible to conduct measurements with it in current experimental setup.

Based on the above presented results, it was found that the optimal nitrogen content in precursor solution was 0.1 wt. %, for the preparation of a CPE based on nitrogen-doped carbonized hydrothermal carbon. On the other hand, 30 wt. % of TCP was selected as optimal binder liquid content in the mentioned CPE.

Fig. 3 shows SEM images of carbon material CHTCN0.1 (a) and CPE based on CHTCN0.1 and TCP (b). In general, the morphology of CHTCN0.1 is the char-acteristic morphology for hydrothermal carbons obtained from glucose at a lower temperature, which consists of micrometric spheres with a smooth surface and with the inhomogeneous diameter size, in this case from 0.5 to 3 µm.48 The image of CPE (Fig. 3b) shows the graphite particles coated with liquid binder and matted, and the cavities which are formed between them.

Fig. 3. SEM images of CHTCN0.1 (a) and CPE/CHTCN0.1 (b).

pH-Dependence of carbendazim oxidation The effect of pH on the electrochemical response of carbendazim was inves-

tigated in the pH range from 2.0 to 8.0 in Britton–Robinson buffer solutions using a DPV method. DPV method was also involved for examination of pH

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effect on the electrochemical response of carbendazim for CPE/CHTCN0.05 and CPE/CHTCN0.5. The satisfying electroanalytical responses regarding carbenda-zim were not obtained for any of the two CPEs since the oxidation peaks were significantly lower in intensity and shifted toward higher potential compared to results obtained for CPE/CHTCN0.1. Consequently, these two electrodes were excluded from further examinations. As shown in Fig. 4, the oxidation peak of carbendazim obtained using CPE/CHTCN0.1 is clearly visible at all pH values, but its intensity and position were clearly dependent on pH. The most intense peak was obtained in acidic media at pH 3.0 (at 0.98 V), therefore this pH was selected for further experiments. The shift of the oxidation peak potential toward negative value with increasing pH from 2 to 6 indicated that the protons are involved in the electrode reaction.

Fig. 4. DPSV curves of carbendazim (c = 1.3 μg cm-3) at CPE/ /CHTCN0.1 in different Britton–Robinson buffer sol-utions (pH range from 2.0 to 8.0).

Repeatability and stability of CPE/CHTCN0.1 The repeatability and stability of CPE/CHTCN0.1 were also evaluated. The

relative standard deviation (RSD) for detection of 125 ng cm–3 carbendazim at pH 3.0 at five independently prepared electrodes was 4.5 %, which shows good rep-eatability of the CPE/CHTCN0.1. The stability (aging of the electrode) is also an important parameter for the evaluation of the electrode. The electrode surface was covered and stored in the fridge when not in use. After 5 days of storing the electrode gave 96 % of its initial peak current value. 90 % of the initial response still remained after 4 weeks of storage, confirming that the CPE/CHTCN0.1 had also an acceptable storage stability.

Because of the adsorption behaviour of carbendazim at CPE/CHTCN0.1 sur-face, the electrode can not be reused directly after measurements. It is necessary to renew its surface and then activate it by potential cycling (10 cycles in the range from –0.2 to 1.6 V using scan rate of 250 mV s–1) in an adequate Britton– –Robinson buffer.

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Optimization of DPSV parameters The optimal conditions for DPSV determination of carbendazim were care-

fully selected. It was found that the oxidation peak current intensity changes with the accumulation potential, Eacc in the investigated range from 0.15 and 0.55 V. As shown in Fig. 5a, the peak current increased to its maximum at –0.15 V and then started to decrease, so –0.15 V was selected as optimal accumulation pot-ential. When the accumulation time, tacc was changed from 5 to 300 s (Fig. 5b), the oxidation peak current increased gradually to the maximum value at 80 s and then with further increase of the accumulation time, the peak current slightly decreased. Therefore, 80 s was chosen as optimal tacc.

Fig. 5. Optimization of accumulation potential (a) and accumulation time (b) in DPSV of

carbendazim (c = 1.3 μg cm-3) at pH 3.0.

Quantitative determination of carbendazim in model solution Fig. 6 shows DPSV responses of different concentrations of carbendazim on

CPE/CHTCN0.1 under the optimal conditions in the concentration range from 25 to 490 ng cm–3 (Fig. 6a), together with the corresponding calibration plot (Fig. 6b). Dependence of peak current intensity (ip) on the carbendazim concentration

Fig. 6. DPSV determination of carbendazim at CPE/CHTCN0.1 in the concentration range

from 25 to 490 ng cm-3 (a) together with corresponding calibration plot (b).

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(c) could be described using the following equation: ip = 1.62128c – 0.0281, with a correlation coefficient of 0.9983. The reproducibility of the analytical response was assessed by comparing the heights of the peak current of seven consecutive recordings at carbendazim concentration level of 125 ng cm–3. The RSD value of 2.9 % indicates a relatively good precision of the developed method. The detect-ion limit (LOD) and the quantitation limit (LOQ) were determined using the 3σ/S and 10σ/S criterion, where σ is the estimated standard deviation of the peak height intensity for the lowest measured concentration (6 measurements) and S is the slope of the calibration curve. The calculated LOD and LOQ were 1.24 and 4.04 ng cm–3, respectively. Considering all above results, it is clear that the pro-posed electrode can be successfully applied for the quantitative determination of carbendazim in model solution at very low concentration levels.

Investigation of the interferences The interference of some common ions (Na+, K+, Ca2+, Ag+, Cl–, CO3

2–, HCO3

– and NO3-) and pesticides (dimethoate, imidacloprid, tebufenozide and

simazine), on the determination of carbendazim, was also tested in this study. Firstly, DPSV signal of carbendazim (125 ng cm–3) was recorded using the CPE/ /CHTCN0.1, then either selected ion was added in a concentration that is 50 times higher than carbendazim, or a selected pesticide was added in the same final con-centration as carbendazim. The solutions were analyzed by the proposed method and all investigated ions or pesticides neither influenced peak potential nor oxidation peak current intensity of carbendazim significantly.

Analysis of real samples The applicability of the developed voltammetric procedure was also tested

for the determination of carbendazim in tap and river water (Danube) samples spiked with 50 ng cm–3 of carbendazim, which was further diluted to 25 ng cm–3 with Britton–Robinson buffer pH 3.0 in 1:1 volume ratio (Fig. 7).

Before spiking, samples did not contain any detectable amount of the ana-lyte. Standard addition method was applied in all determinations (Fig. 7b and d), which were done in triplicate. As can be seen, the matrix from the water samples did not block the electrode surface and did not show voltammetric interferences, which are favourable facts for determination (Fig. 7a and c). Peak height inten-sities of carbendazim were comparable to the corresponding ones in case of model solutions. The peak potential differs just a slightly from this of the model solution and it has around 0.03 V more positive values. On the other hand, good correlation between the added and found carbendazim amounts in spiked water samples (recovery was 103.70 % for tap water and 102.78 % for Danube water) and low RSDs (4.1 and 4.3 %, respectively) reflected high accuracy and precision of the proposed DPSV method even at such low concentration level.

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Fig. 7. Determination of carbendazim in spiked water samples using DPSV: Tap water sample (a) with the corresponding standard addition plot (b) and Danube river water sample (c) with

the corresponding standard addition plot (d).

CONCLUSIONS

A novel carbon paste electrode based on simple and low-cost produced, nit-rogen-doped hydrothermal carbon was successfully fabricated. Carbonized hyd-rothermal carbon sample with 0.1 wt. % nominal nitrogen concentration as a carbon component and 30 wt. % of tricresyl phosphate as a liquid binder were the selected components for the preparation of carbon paste electrode with the best electrochemical response toward Fe(CN)6

3–/4– redox couple. On the other hand, a differential pulse stripping voltammetric method was developed for the deter-mination of carbendazim fungicide. The method offered linearity in a wide con-centration range from 25 to 490 ng cm–3 with an estimated low detection limit of 1.21 ng cm–3. Several advantageous characteristics of the new electrode such as good stability, high selectivity, and excellent repeatability were also reported. Furthermore, the electrode was successfully applied for the determination of car-bendazim traces in spiked tap and river water samples with high precision and recovery. The overall results showed that the nitrogen-doped hydrothermal car-bon is a good candidate as a material for the preparation of carbon paste elec-trodes, which could find broad application in electroanalysis.

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SUPPLEMENTARY MATERIAL Effect of TCP mass fraction in CPE/CHTCN0.1 on cyclic voltammograms of Fe(CN)6

3-/4- redox couple are available electronically from http://www.shd.org.rs/JSCS/, or from the cor-responding author on request.

Acknowledgments. We acknowledge the support to this work provided by the Ministry of Education, Science and Technological Development of Serbia through project Physics and Chemistry with Ion Beams No. III 45006.

И З В О Д ЕЛЕКТРОХЕМИЈСКО ОДРЕЂИВАЊЕ КАРБЕНДАЗИМА НОВОМ ЕЛЕКТРОДОМ ОД УГЉЕНИЧНЕ ПАСТЕ БАЗИРАНЕ НА АЗОТОМ ДОПИРАНОМ ХИДРОТЕРМАЛНОМ

УГЉЕНИКУ

АНА КАЛИЈАДИС1, ЈЕЛЕНА ЂОРЂЕВИЋ1, ZSIGMOND PAPP2, БОЈАН ЈОКИЋ3, ВУК СПАСОЈЕВИЋ1, БИЉАНА БАБИЋ1 и ТАТЈАНА ТРТИЋ-ПЕТРОВИЋ1

1Институт за нуклеарне науке Винча, Универзитет у Београду, Мике Петровића Аласа 12–14, 11001 Београд, 2Факултет за биофарминг, Универзитет Џон Незбит, Маршала Тита 39, 24300 Бачка

Топола и 3Технолошко–металуршки факултет, Универзитет у Београду, Карнегијева 4, 11000 Београд

У овом раду направљена је нова електрода од угљеничне пасте на бази азотом допираног хидротермалног угљеника, која је примењена у електрохемијскoм одређи-вању фунгицида карбендазима. Допирани узорци хидротермалног угљеника номиналне концентрације азота у опсегу 0,05–0,5 масених процената у полазном раствору глукозе, синтетисани су јефтиним поступком, који је праћен накнадном карбонизацијом до 1273 K. Присуство азота потврђено је методом елементалне анализе. Карактеризација синте-тисаних узорака као материјала за припрему електрода од угљеничне пасте базирала се на електрохемијским испитивањима Fe(CN)6

3–/4– редокс пара, која су показала да нај-бољи електрохемијски одговор даје узорак са номиналоном концентрацијом азота од 0,1 мас. % и трикрезил фосфатом као везујућим средством. Током развијања методе дифе-ренцијалне пулсне стрипинг волтаметрије за одређивање карбендазима применом нове електроде, праћени су следећи експериментални параметри: тип и количина везујућег средства, pH, акумулациони потенцијал и акумулационо време. Резултати су показали да се под оптималним условима добија линеарност за широки опсег концентрација од 25 до 490 ng cm-3, као и граница детекције од 1,21 ng cm-3. Закључено је да електрода бази-рана на азотом допираном хидротермалном угљенику показује добру стабилност и ви-соку селективност, као и да је развијени метод успешно примењен за одређивање тра-гова карбендазима, како у спајкованим, тако и у реалним узорцима воде.

(Примљено 28. децембра 2016, ревидирано 28. априла, прихваћено 15. маја 2017)

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